NSW Arbovirus Surveillance & Vector Monitoring Program
1999 - 2000 Annual Report

bottom of page

DISCUSSION

The moist conditions that marked the end of the drought in 1998 continued into 1999, with rainfall being mostly above average across the state for 1999-2000. Despite this, mosquito numbers failed to reach extremely high numbers during peak season. This appeared to be due to the cold summer temperatures, with some areas up to 60C below average. Autumn however, was quite mild and warm, and mosquito numbers remained stable and above average until the end of April. Thus, while the overall number of mosquitoes was not as high as the previous season, the 245,524 mosquitoes collected during 1999-2000 was the second highest number trapped by the program.  

The only locations that had very high mosquito densities were those from the northwest, where mosquitoes were extremely abundant following the heavy February rains. Numbers at Fords Bridge were especially high, with over 10,000 mosquitoes collected from one trap in late March. These collections were dominated by floodwater Aedes species, notably Aedes eidsvoldensis and Aedes theobaldi, and several new mosquito species for the program were identified including Aedes Marks no.71, Aedes Marks no.85, Aedes sapiens and Culex starckeae. Mimomyia elegans was also collected during these floods, which is a new program record for the northwest. Along with these mosquitoes was some late virus activity, with two isolates each of RR and SIN from Fords Bridge in late March/early April. The isolates of RR and SIN from Aedes eidsvoldensis and the RR from Aedes theobaldi at Fords Bridge represent new mosquito/virus records for NSW.  

As noted above, there were several new mosquito records from the northwest and Culex orbostiensis was trapped for the first time from the inland at Deniliquin. An additional record for the state was one specimen similar to Culex gelidus collected from the Sewerage Treatment Works at Condobolin in March 2000. This is an exotic species, first recognised in Australia from Brisbane in June 1999 (Muller, 1999). Since then, it has been found to be widespread along coastal Queensland (Ritchie & Haselar, 2000), throughout inland Northern Territory (Whelan et al., 2000) and was recently discovered in Western Australia (Dr Michael Lindsay, WA Health Department, pers. comm.). Immediately after the collection of the NSW specimen, staff from the Entomology Department (SD & RCR) undertook an intensive larval survey with adult trapping at Condobolin but no further specimens were revealed. The concern is that Culex gelidus, a known vector of Japanese Encephalitis, often breeds in polluted waters where Culex annulirostris fails to thrive, thus if the Culex gelidus becomes established in NSW, it will supplement the known mosquito vectors. Continual monitoring for this species is essential.  

In most years, Culex annulirostris comprises around 80% of all mosquitoes trapped from the inland. For this season it was only around 60%, due to the high number of Aedes trapped in the northwest, which constituted 10% of the inland mosquitoes. However, Culex annulirostris continues to yield the majority of inland viruses with 16 isolates (11 RR and 5 SIN). Anopheles annulipes was again the second most common inland species, comprising roughly 20% of the collections, and 8 viruses (3 RR and 5 unknowns) were isolated from this species.  

As stated above, there was no evidence of any MVE in NSW, despite one of the environmental models suggesting possible activity. However, there has been widespread activity with associated human cases during 2000 in Western Australia, the Northern Territory and in the north of South Australia (Broom & Whelan, 2000). As evidence suggests that MVE is introduced via viraemic migratory birds from endemic regions of the north (Marshall, 1988), several new trap sites were established in the northwest including Wanaaring and Fords Bridge. The expectation is that if MVE does come from the north into NSW, then it will be detected before reaching the more populated areas of the south. In light of northern MVE cases, and that both the Forbes’ and Nicholls’ hypotheses are suggesting MVE activity in 2000-2001, it will be critical that monitoring of weather patterns continue into 2000. Relevant environmental conditions appear on the NSW Arbovirus Surveillance web site.  

The number of chicken flocks was increased this year to nine, with eight surveillance locations. Due to the MVE activity in central Australia and the high rainfall in the northwest, testing of the flocks in the northwest was extended through May. There were no seroconversions in the NSW flocks.  

The mosquito numbers from the north coast were mostly down on average, although there were several large collections in late March/early April from Ballina with freshwater mosquitoes dominating. South coast numbers continued to be very low due to the dry summer conditions, and arbovirus activity has been low since the Barmah Forest outbreak in 1994-1995 (Doggett et al., 1999). This would suggest that both animal reservoirs and the human population would be becoming increasingly susceptible to arboviral infection and at risk of major activity. Continued monitoring of this region is highly advisable. New mosquito records for the coast include Aedes bancroftianus trapped at Port Stephens and Anopheles amictus collected from the Hawkesbury traps.  

The number of Sydney surveillance locations was also reduced this season, with emphasis being placed on the Western Sydney locations where RR activity has occurred over the last three years. As per elsewhere, mosquito numbers were down with the cold temperatures. There were no viral isolates from the mosquitoes. A small number of locally acquired cases of RR were identified in Western Sydney, although notifications were down upon previous years.  

Human disease notifications in 1999-2000 contrasted strongly with the previous season.  In 1998, the heavy rains led to enormous mosquito numbers in the southern inland regions and the surveillance resulted in a RR mosquito isolate from the first week of November. Eventually, record numbers of human RR cases were reported from this region during late spring/summer. For 1999-2000, the heavy rains in the same period did not lead to large mosquito numbers, there were no early arbovirus isolates and human cases were relatively few. The late mosquito and arbovirus activity in the northwest occurred in a sparsely populated region, and hence there was no significant rise in notifications. The only Area Heath Service to have more notifications than last season was the Mid North Coast. Interestingly, this was the region where all arbovirus surveillance activities were stopped prior to the 1999-2000 season.

Back to Contents

top of page